CN101270334B - Isolated culture method for anaerobic microorganism - Google Patents
Isolated culture method for anaerobic microorganism Download PDFInfo
- Publication number
- CN101270334B CN101270334B CN2007100647153A CN200710064715A CN101270334B CN 101270334 B CN101270334 B CN 101270334B CN 2007100647153 A CN2007100647153 A CN 2007100647153A CN 200710064715 A CN200710064715 A CN 200710064715A CN 101270334 B CN101270334 B CN 101270334B
- Authority
- CN
- China
- Prior art keywords
- anaerobic
- bacteria
- tube
- medium
- copper wire
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- 244000005700 microbiome Species 0.000 title claims abstract description 22
- 238000012136 culture method Methods 0.000 title 1
- 241000894006 Bacteria Species 0.000 claims abstract description 38
- 238000000034 method Methods 0.000 claims abstract description 24
- 238000002955 isolation Methods 0.000 claims abstract description 10
- 239000002609 medium Substances 0.000 claims description 25
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims description 20
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 19
- 229920001817 Agar Polymers 0.000 claims description 11
- 239000008272 agar Substances 0.000 claims description 11
- 229910052757 nitrogen Inorganic materials 0.000 claims description 10
- 239000001963 growth medium Substances 0.000 claims description 9
- SURQXAFEQWPFPV-UHFFFAOYSA-L iron(2+) sulfate heptahydrate Chemical compound O.O.O.O.O.O.O.[Fe+2].[O-]S([O-])(=O)=O SURQXAFEQWPFPV-UHFFFAOYSA-L 0.000 claims description 8
- 239000011521 glass Substances 0.000 claims description 7
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 6
- 239000007788 liquid Substances 0.000 claims description 6
- 206010027146 Melanoderma Diseases 0.000 claims description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 4
- 229920000742 Cotton Polymers 0.000 claims description 4
- ATJFFYVFTNAWJD-UHFFFAOYSA-N Tin Chemical compound [Sn] ATJFFYVFTNAWJD-UHFFFAOYSA-N 0.000 claims description 4
- 229910052799 carbon Inorganic materials 0.000 claims description 4
- 239000003550 marker Substances 0.000 claims description 4
- 239000006228 supernatant Substances 0.000 claims description 4
- 241001148471 unidentified anaerobic bacterium Species 0.000 abstract description 29
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 15
- 239000001301 oxygen Substances 0.000 abstract description 15
- 229910052760 oxygen Inorganic materials 0.000 abstract description 15
- 238000011160 research Methods 0.000 description 10
- 239000000523 sample Substances 0.000 description 7
- 238000000926 separation method Methods 0.000 description 7
- 238000012163 sequencing technique Methods 0.000 description 6
- 108020004465 16S ribosomal RNA Proteins 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 239000005445 natural material Substances 0.000 description 3
- 230000001580 bacterial effect Effects 0.000 description 2
- 244000052616 bacterial pathogen Species 0.000 description 2
- 239000011248 coating agent Substances 0.000 description 2
- 238000000576 coating method Methods 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 230000003203 everyday effect Effects 0.000 description 2
- 230000000813 microbial effect Effects 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 239000002352 surface water Substances 0.000 description 2
- FRXSZNDVFUDTIR-UHFFFAOYSA-N 6-methoxy-1,2,3,4-tetrahydroquinoline Chemical compound N1CCCC2=CC(OC)=CC=C21 FRXSZNDVFUDTIR-UHFFFAOYSA-N 0.000 description 1
- 241000186031 Corynebacteriaceae Species 0.000 description 1
- 241000590002 Helicobacter pylori Species 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- VMHLLURERBWHNL-UHFFFAOYSA-M Sodium acetate Chemical compound [Na+].CC([O-])=O VMHLLURERBWHNL-UHFFFAOYSA-M 0.000 description 1
- 208000005718 Stomach Neoplasms Diseases 0.000 description 1
- 241000812944 Thioclava pacifica Species 0.000 description 1
- 241001148470 aerobic bacillus Species 0.000 description 1
- 238000012364 cultivation method Methods 0.000 description 1
- 238000003745 diagnosis Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000003933 environmental pollution control Methods 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 206010017758 gastric cancer Diseases 0.000 description 1
- 238000010353 genetic engineering Methods 0.000 description 1
- 230000009036 growth inhibition Effects 0.000 description 1
- 229940037467 helicobacter pylori Drugs 0.000 description 1
- 231100001240 inorganic pollutant Toxicity 0.000 description 1
- 239000011229 interlayer Substances 0.000 description 1
- 230000002503 metabolic effect Effects 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 150000007523 nucleic acids Chemical group 0.000 description 1
- 230000007170 pathology Effects 0.000 description 1
- 230000035479 physiological effects, processes and functions Effects 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000005096 rolling process Methods 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 235000017281 sodium acetate Nutrition 0.000 description 1
- 239000001632 sodium acetate Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 241000894007 species Species 0.000 description 1
- 230000001954 sterilising effect Effects 0.000 description 1
- 238000004659 sterilization and disinfection Methods 0.000 description 1
- 201000011549 stomach cancer Diseases 0.000 description 1
- 241001300301 uncultured bacterium Species 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Images
Landscapes
- Measuring Or Testing Involving Enzymes Or Micro-Organisms (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
本发明涉及一种厌氧微生物分离培养方法,该方法在整个操作过程中避免了目的微生物与氧气的接触,操作成本相对低廉,尤其适于生长温度高于50℃且对厌氧环境要求严格的难分离高温厌氧菌、严格厌氧菌。该方法只需在厌氧菌分离的部分操作时使用厌氧工作站,培养时可以使用普通培养箱,无需继续提供厌氧环境,避免了分离培养时一台厌氧工作站只能用于一种生长温度的细菌的情况;对于培养温度高于厌氧工作站温度上限的细菌,该方法同样适用。The invention relates to a method for isolating and cultivating anaerobic microorganisms. The method avoids the contact of target microorganisms with oxygen during the whole operation process, and the operation cost is relatively low. It is especially suitable for those whose growth temperature is higher than 50°C and which have strict requirements on anaerobic environment. Difficult to separate high temperature anaerobic bacteria, strict anaerobic bacteria. This method only needs to use the anaerobic workstation for part of the operation of anaerobic bacteria isolation, and can use an ordinary incubator for cultivation, without continuing to provide an anaerobic environment, avoiding that an anaerobic workstation can only be used for one kind of growth during isolation and cultivation This method is also applicable to bacteria whose culture temperature is higher than the upper limit of the anaerobic workstation.
Description
发明领域field of invention
本发明涉及一种厌氧微生物的分离方法,尤其是一种极端微生物生理生态研究、自然生态研究,遗传工程研究,生命科学研究,病理学研究,海洋地质研究和环境污染治理中不可缺少的新方法。The present invention relates to a method for separating anaerobic microorganisms, in particular to an indispensable new method for extremophile physiological ecology research, natural ecology research, genetic engineering research, life science research, pathology research, marine geological research and environmental pollution control. method.
背景技术Background technique
在自然生态系统中,微生物扮演着非常重要的角色。在污染治理中,微生物可以分解很多其他方法不能去除的有机或无机污染物,且成本低廉;在地质学研究中,不同区域的特定种类的极端微生物的亲缘关系,可能标志着这些区域以往的位置关系。但微生物往往是以菌群为单位,多种微生物生存在一起,因此,分离获得微生物的纯培养是微生物生理生化研究中必须首先解决的问题。一个新的微生物菌种的发现,往往会导致微生物学的重大进展,也可能会引起一个新的学科交叉点:比如硝酸盐还原菌与硝酸盐废水的治理,幽门螺旋菌与胃癌的治疗等。其中,极端环境下的微生物往往是环境、能源、地质研究中比较重要的角色,可以给科研工作者提供很多新的思路和方法。但由于其培养的环境条件难以在常规条件下得到模拟,极端环境下的微生物往往是难以纯化培养,尤其是要求几种极端条件同时具备的情况,如要求极端厌氧环境和高温环境同时具备。In natural ecosystems, microorganisms play a very important role. In pollution control, microorganisms can decompose many organic or inorganic pollutants that cannot be removed by other methods, and the cost is low; in geological research, the kinship of specific types of extremophiles in different regions may mark the previous location of these regions relation. However, microorganisms are often based on flora as a unit, and a variety of microorganisms live together. Therefore, the isolation and pure culture of microorganisms is a problem that must be solved first in the study of microbial physiology and biochemistry. The discovery of a new microbial strain often leads to significant progress in microbiology, and may also lead to a new interdisciplinary point: such as the treatment of nitrate-reducing bacteria and nitrate wastewater, Helicobacter pylori and the treatment of gastric cancer, etc. Among them, microorganisms in extreme environments often play an important role in environmental, energy, and geological research, which can provide researchers with many new ideas and methods. However, because the environmental conditions for their cultivation are difficult to simulate under conventional conditions, it is often difficult to purify and cultivate microorganisms in extreme environments, especially when several extreme conditions are required at the same time, such as an extreme anaerobic environment and a high temperature environment.
微生物的分离和纯化的方法及专利有很多,如一次性微生物分离诊断鉴定培养基(专利号:200520003682.8),一种微生物分离培养方法(专利号:94103474.7)等,但这些分离方法中,多数为针对分离好氧菌或兼性厌氧菌。There are many methods and patents for the isolation and purification of microorganisms, such as a disposable microorganism isolation diagnosis and identification medium (patent number: 200520003682.8), a microorganism isolation and cultivation method (patent number: 94103474.7), etc., but most of these isolation methods are For isolating aerobic or facultative anaerobic bacteria.
厌氧菌分为非严格厌氧菌和严格厌氧菌:暴露于氧气中会造成生长抑制的细菌为非严格厌氧菌,暴露于氧气中造成菌体死亡的称为严格厌氧菌。不同厌氧菌对氧气的耐受能力不同,一般以耐氧时间作为指标。在耐氧时间内,不会造成菌体死亡,菌体的耐氧时间差异很大,从几秒钟到数十小时不等。对于耐氧时间极短的细菌,由于在分离操作的过程中很容易因接触氧气而造成菌体死亡,人们往往很难分离到,只能用探针的方法去检测其核酸片断,无法得到纯培养细菌。而耐氧时间短的细菌多数生活在极端环境中,如在深海中由于巨大的水压,细菌不会和氧气接触。极端环境微生物往往是一个新的物种,对科学研究的意义重大;而且由于极端条件下的样品很难获得,所以,从极端条件下分离到的微生物十分珍贵。但是,这种对厌氧条件的严格要求造成了分离厌氧菌的极大的障碍。如果没有得到细菌的纯培养,人们就难以在自然的条件下去研究该厌氧菌的代谢机理,对厌氧菌进一步研究受到制约。在对厌氧细菌的检索中,有很多细菌均被称为“未培养细菌”。这说明对于厌氧细菌来说,现有的分离技术还有很大的局限性。Anaerobic bacteria are divided into non-strict anaerobic bacteria and strict anaerobic bacteria: bacteria that will cause growth inhibition when exposed to oxygen are non-strict anaerobic bacteria, and bacteria that cause bacterial death when exposed to oxygen are called strict anaerobic bacteria. Different anaerobic bacteria have different tolerance to oxygen, and the oxygen tolerance time is generally used as an indicator. During the oxygen resistance time, the bacteria will not die, and the oxygen resistance time of the bacteria varies greatly, ranging from a few seconds to tens of hours. For bacteria with a very short oxygen resistance time, because it is easy to cause bacterial death due to contact with oxygen during the separation operation, it is often difficult for people to separate them, and the nucleic acid fragments can only be detected by the probe method, and pure bacteria cannot be obtained. cultivate bacteria. Most of the bacteria with short oxygen resistance time live in extreme environments, such as in the deep sea, due to the huge water pressure, the bacteria will not come into contact with oxygen. Microorganisms in extreme environments are often a new species, which is of great significance to scientific research; and because samples under extreme conditions are difficult to obtain, microorganisms isolated from extreme conditions are very precious. However, this strict requirement for anaerobic conditions creates a great obstacle for isolating anaerobic bacteria. If the pure culture of bacteria is not obtained, it is difficult for people to study the metabolic mechanism of the anaerobic bacteria under natural conditions, and further research on anaerobic bacteria is restricted. In the search for anaerobic bacteria, many bacteria are called "uncultured bacteria". This shows that for anaerobic bacteria, the existing separation technology still has great limitations.
目前已报道分离厌氧细菌的方法主要有:The main methods for isolating anaerobic bacteria have been reported so far:
1)利用厌氧工作站对细菌进行分离培养,可以保证分离的全过程中,目的细菌与氧气隔绝,但是,目前的厌氧工作站中一般设定的培养温度上限为50℃,难以给嗜热厌氧菌提供足够的培养温度。而且即使欲分离培养50℃以下生长环境的细菌,一个厌氧工作站只也能设定一个培养温度,分离培养不同温度的微生物就需要多个厌氧工作站,极大的提高了实验成本。同时,厌氧工作站中难以提供严格的无菌环境,培养时,培养皿之间容易互相染菌。1) Using an anaerobic workstation to isolate and cultivate bacteria can ensure that the target bacteria are isolated from oxygen during the whole process of isolation. However, the upper limit of the culture temperature generally set in the current anaerobic workstation is 50 ° C, which is difficult to give thermophilic anaerobic bacteria. Aerobic bacteria provide sufficient culture temperature. Moreover, even if it is desired to isolate and cultivate bacteria in a growth environment below 50°C, one anaerobic workstation can only set one cultivation temperature, and to isolate and cultivate microorganisms at different temperatures requires multiple anaerobic workstations, which greatly increases the cost of the experiment. At the same time, it is difficult to provide a strict aseptic environment in the anaerobic workstation, and it is easy to contaminate the petri dishes with each other during cultivation.
2)利用厌氧罐、厌氧袋及滚管操作分离厌氧微生物,可以提供细菌50℃以上的培养温度,但整个操作过程暴露于空气中,目的厌氧菌会与氧气接触,造成目的菌体死亡。2) Using anaerobic tank, anaerobic bag and rolling tube to separate anaerobic microorganisms can provide bacteria with a culture temperature above 50°C, but the whole operation process is exposed to the air, and the target anaerobic bacteria will come into contact with oxygen, resulting in the growth of the target bacteria. body death.
3)文献《一种分离培养硫酸盐还原菌的改进方法》(万海清,应用与环境生物学报,2003,9(5):561-562)中介绍了叠皿夹层法分离厌氧微生物,但该方法在涂布操作过程中,菌体会短时间内暴露于空气中。如果预分离的细菌的耐氧时间较少,将会造成目的菌体的死亡。3) The document "An Improved Method for Isolating and Cultivating Sulphate-Reducing Bacteria" (Wan Haiqing, Journal of Applied and Environmental Biology, 2003, 9(5): 561-562) introduces the separation of anaerobic microorganisms by the stacked dish interlayer method, However, in this method, during the coating operation, the bacterium will be exposed to the air in a short period of time. If the oxygen resistance time of the pre-isolated bacteria is less, it will cause the death of the target bacteria.
4)文献《对一种新的厌氧菌培养皿-OxyplateTM的评估》(赵虎等,上海医学检验杂志,2002,06)中介绍了利用OxyplateTM培养皿分离厌氧菌的方法,该方法同样存在于涂布操作过程中,菌体短时间暴露于空气中,造成菌体死亡。4) The document "Evaluation of a new anaerobic culture dish-OxyplateTM" (Zhao Hu et al., Shanghai Journal of Medical Laboratory, 2002, 06) introduces the method of utilizing the OxyplateTM culture dish to separate anaerobic bacteria. During the coating operation, the bacteria are exposed to the air for a short time, resulting in the death of the bacteria.
5)专利一种适合厌氧培养使用的培养皿,(专利号:200420074957.2),该专利针对医疗基层机构中厌氧致病菌的发现和培养,致病菌往往生存在非严格厌氧的环境中,利用这种培养皿分离耐氧时间短的细菌,可能会造成菌体死亡。5) A petri dish suitable for anaerobic culture is patented (patent number: 200420074957.2). This patent is aimed at the discovery and cultivation of anaerobic pathogenic bacteria in medical grass-roots institutions. Pathogenic bacteria often live in a non-strictly anaerobic environment In the process, using this culture dish to isolate bacteria with a short oxygen resistance time may cause the death of the bacteria.
发明内容Contents of the invention
本发明的目的是:提供一种简单且准确的高温厌氧菌分离方法,该方法能够在操作全程中避免目的厌氧菌菌体与空气接触,并且可以分离50℃以上培养温度的高温厌氧菌。The purpose of the present invention is to provide a simple and accurate method for isolating high-temperature anaerobic bacteria, which can avoid the contact of target anaerobic bacteria with air during the whole operation, and can separate high-temperature anaerobic bacteria with a culture temperature above 50°C. bacteria.
本发明的具体解决方案为:Concrete solution of the present invention is:
1)将含指示剂的琼脂培养基及带密封盖的玻璃管灭菌;1) Sterilize the agar medium containing the indicator and the glass tube with a sealed cover;
2)将未凝固的琼脂培养基、含目的厌氧菌的自然物质、带密封盖的玻璃管放入厌氧工作站的样品室中,向样品室中进行反复三次的抽空气,冲入氮气(或氢氮混合气)的常规操作;2) Put the unsolidified agar medium, the natural substance containing the target anaerobic bacteria, and the glass tube with a sealed cover into the sample chamber of the anaerobic workstation, repeatedly pump air into the sample chamber three times, and flush nitrogen ( or hydrogen-nitrogen mixture) for routine operation;
3)将含目的微生物的自然物质与未凝固的琼脂培养基混合均匀后,分装于玻璃管中,旋紧密封盖;3) After mixing the natural substances containing the target microorganisms and the unsolidified agar medium evenly, divide them into glass tubes, and tighten the sealing caps;
4)从厌氧工作站中将玻璃管取出,置于培养箱中,设定培养温度,培养一定时间;4) Take out the glass tube from the anaerobic workstation, place it in the incubator, set the cultivation temperature, and cultivate for a certain period of time;
5)待玻璃管中有阳性反应(与所加指示剂的阳性反应一致)时,在厌氧操作站中,将目的菌体取出。5) When there is a positive reaction in the glass tube (consistent with the positive reaction of the added indicator), take out the target bacteria in the anaerobic operation station.
本发明的优点如下:The advantages of the present invention are as follows:
1.分离速度快,富集液到分离到菌体的时间在一周之内,且纯度非常高;1. The separation speed is fast, the time from the enrichment solution to the separation of the bacteria is within one week, and the purity is very high;
2.达到同样分离效果的操作成本比其它高温厌氧菌的分离方法低;2. The operating cost to achieve the same separation effect is lower than that of other high temperature anaerobic bacteria separation methods;
3.简便易行;3. Easy to operate;
4.可分离到普通方法难以得到的高温厌氧菌。4. It can isolate high-temperature anaerobic bacteria that are difficult to obtain by ordinary methods.
附图说明Description of drawings
图1培养出高温厌氧菌的厌氧管及挖琼脂时用的铜丝Figure 1 The anaerobic tube for cultivating high temperature anaerobic bacteria and the copper wire used for digging agar
1.挖琼脂块时所用到的铜丝1. Copper wire used when digging agar blocks
2.培养出高温厌氧菌的厌氧管2. Anaerobic Tubes for Cultivating Thermoanaerobic Bacteria
图2厌氧工作站示意图Figure 2 Schematic diagram of anaerobic workstation
1.气路系统1. Gas system
2.气密室(用于送样品)2. Airtight chamber (for sending samples)
3.样品3. Sample
4.连通气密室与操作室的通道4. The channel connecting the airtight room and the operating room
5.操作室5. Operating room
具体实施方式Detailed ways
取含有目的厌氧微生物的自然物质(热液口底泥、底表水、厌氧污泥),利用合适的液体培养基富集后,在厌氧工作站内将富集液与未凝固的固体培养基混合,分装于厌氧管,从厌氧工作站中取出,置于不同温度条件下培养,即可分离到目的菌种。Take natural substances containing target anaerobic microorganisms (hydrothermal vent sediment, bottom surface water, anaerobic sludge), enrich them with a suitable liquid medium, and mix the enriched liquid with uncoagulated solids in an anaerobic workstation. The medium is mixed, divided into anaerobic tubes, taken out from the anaerobic workstation, and cultured under different temperature conditions, and the target strain can be isolated.
实施例1Example 1
1.用加有七水合硫酸亚铁(0.0001g/L)指示剂的液体培养基对含目的菌体的太平洋深海热液口底泥2.5g进行富集。1. Enrich 2.5 g of the bottom mud of the Pacific Ocean deep-sea hydrothermal vent containing the target bacteria with the liquid medium added with ferrous sulfate heptahydrate (0.0001g/L) indicator.
2.在有氧条件下,以乙醇(浓度为0.2mL/L)为碳源,七水合硫酸亚铁(0.006g/L)为指示剂,琼脂浓度为1.8g/L,配制培养基50mL,置于带棉塞的三角烧瓶中,高温高压灭菌(121℃,15分钟)。2. Under aerobic conditions, use ethanol (concentration: 0.2mL/L) as carbon source, ferrous sulfate heptahydrate (0.006g/L) as indicator, agar concentration as 1.8g/L, prepare medium 50mL, Place in a Erlenmeyer flask with a cotton stopper, and sterilize under high temperature and high pressure (121° C., 15 minutes).
3.在培养基凝固以前,将三角烧瓶和富集液置于厌氧工作站的样品室中,抽氮气充氮气反复三次,抽走培养基内的空气。3. Before the culture medium is solidified, place the Erlenmeyer flask and the enrichment solution in the sample chamber of the anaerobic workstation, pump nitrogen and fill it with nitrogen repeatedly three times, and remove the air in the culture medium.
4.在厌氧工作站的操作箱中,在未凝固的培养基中接入3mL的富集上清液,摇匀后分装于厌氧管(或有密闭性良好的螺口塞的透明玻璃管)中。4. In the operation box of the anaerobic workstation, add 3mL of the enriched supernatant to the uncoagulated medium, shake well and distribute it into anaerobic tubes (or transparent glass with well-tight screw plugs) tube).
5.将厌氧管取出,放入普通培养箱中,调节温度为90℃,60小时后,可观察到培养基内部有小黑点(与指示剂反应的显色现象)出现,继续培养2天,会有不同大小,出现先后时间不同的小黑点,用记号笔在管壁上标记。5. Take out the anaerobic tube, put it into an ordinary incubator, and adjust the temperature to 90°C. After 60 hours, it can be observed that there are small black spots (color development phenomenon that reacts with the indicator) inside the medium, and continue to cultivate for 2 Every day, there will be small black spots of different sizes and different times, which are marked on the tube wall with a marker pen.
6.将铜丝的一端砸平,将这段平的部分弯成钩状,用锡纸包好这样的一小捆铜丝后,灭菌。6. Flatten one end of the copper wire, bend the flat part into a hook shape, wrap such a small bundle of copper wire with tin foil, and then sterilize.
7.将灭菌的铜丝和厌氧管置于厌氧工作站中,用铜丝的弯的一端将小黑点挖出,接种于新的培养基即可。为了保证分到的细菌的纯度,操作时,要从管口处向管内依次挖出小黑点,每挖出一个小黑点前,更换一根新的灭菌铜丝;每挖出一个小黑点后,要将从这个小黑点到管口之间所有的琼脂挖出来。7. Place the sterilized copper wire and anaerobic tube in the anaerobic workstation, dig out the small black spots with the bent end of the copper wire, and inoculate them in new medium. In order to ensure the purity of the bacteria distributed, during operation, small black spots should be dug out from the mouth of the tube to the inside of the tube one by one. Before each small black spot is dug out, a new sterilized copper wire should be replaced; After the black spot, dig out all the agar from the small black spot to the mouth of the tube.
8.对分离得到的目的厌氧菌进行DNA的提取,在利用PCR做16s rDNA测序时不会出现双峰,测序结果准确,在NCBI数据库比对结果表明该菌与一株格兰氏阳性嗜温菌最为相近,相似度99%。8. Extract the DNA of the isolated target anaerobic bacteria. When PCR is used for 16s rDNA sequencing, no double peaks will appear, and the sequencing results are accurate. The comparison results in the NCBI database show that the bacteria is compatible with a Gram-positive strain. The warm bacteria are the most similar, with a similarity of 99%.
实施例2Example 2
1.用加有七水合硫酸亚铁(0.0005g/L)指示剂的液体培养基对含目的菌体的大西洋深海热液口底泥3g进行富集。1. Enrich 3 g of the Atlantic deep-sea hydrothermal vent bottom mud containing the target thalline with the liquid medium added with ferrous sulfate heptahydrate (0.0005g/L) indicator.
2.在有氧条件下,以乙醇(浓度为10mL/L)为碳源,七水合硫酸亚铁(0.0005g/L)为指示剂,琼脂浓度在0.03g/L,配制培养基15mL,置于带棉塞的三角烧瓶中,高温高压灭菌(121℃,15分钟)。2. Under aerobic conditions, use ethanol (concentration of 10mL/L) as carbon source, ferrous sulfate heptahydrate (0.0005g/L) as indicator, and agar concentration at 0.03g/L, prepare medium 15mL, set In a Erlenmeyer flask with a cotton stopper, high temperature and high pressure sterilization (121° C., 15 minutes).
3.在培养基凝固以前,将三角烧瓶和富集液置于厌氧工作站的样品室中,抽氮气充氮气反复三次,抽走培养基内的空气。3. Before the culture medium is solidified, place the Erlenmeyer flask and the enrichment solution in the sample chamber of the anaerobic workstation, pump nitrogen and fill it with nitrogen repeatedly three times, and remove the air in the culture medium.
4.在厌氧工作站的操作箱中,在未凝固的培养基中接入3mL的富集上清液,摇匀后分装于厌氧管中。4. In the operation box of the anaerobic workstation, add 3mL of the enriched supernatant to the uncoagulated medium, shake well and distribute into anaerobic tubes.
5.将厌氧管取出,放入普通培养箱中,调节温度为60℃,35小时后,可观察到培养基内部有小黑点(与指示剂反应的显色现象)出现,继续培养4天,会有不同大小,出现先后时间不同的小黑点,用记号笔在管壁上标记。5. Take out the anaerobic tube, put it into an ordinary incubator, and adjust the temperature to 60°C. After 35 hours, it can be observed that there are small black spots (color development phenomenon that reacts with the indicator) inside the medium, and continue to cultivate for 4 Every day, there will be small black spots of different sizes and different times, which are marked on the tube wall with a marker pen.
6.将铜丝的一端砸平,将这段平的部分弯成钩状,用锡纸包好这样的一小捆铜丝后,灭菌。6. Flatten one end of the copper wire, bend the flat part into a hook shape, wrap such a small bundle of copper wire with tin foil, and then sterilize.
7.将灭菌的铜丝和厌氧管置于厌氧工作站中,用铜丝的弯的一端将小黑点挖出,接种于新的培养基即可。7. Place the sterilized copper wire and anaerobic tube in the anaerobic workstation, dig out the small black spots with the bent end of the copper wire, and inoculate them in new medium.
8.对分离得到的目的厌氧菌进行DNA的提取,在利用PCR做16s rDNA测序时不会出现双峰,测序结果准确,在NCBI数据库结果表明该菌与一株厌氧嗜温菌最为相近,相似度100%。8. Extract the DNA of the isolated target anaerobic bacteria. When PCR is used for 16s rDNA sequencing, no double peaks will appear, and the sequencing results are accurate. The results in the NCBI database show that the bacteria is most similar to an anaerobic mesophilic bacteria , 100% similarity.
实施例3Example 3
1.用加有七水合硫酸亚铁(0.02g/L)指示剂的液体培养基对含目的菌体的太平洋近海底表水3-10mL进行富集。1. Enrich 3-10mL of the surface water near the bottom of the Pacific Ocean containing the target bacteria with a liquid medium added with ferrous sulfate heptahydrate (0.02g/L) indicator.
2.在有氧条件下,以乙酸钠(浓度为8g/L)为碳源,七水合硫酸亚铁(0.02g/L)为指示剂,琼脂浓度为0.03g/L,配制培养基100mL,置于带棉塞的三角烧瓶中,高温高压灭菌(121℃,15分钟)。2. Under aerobic conditions, sodium acetate (concentration is 8g/L) is used as carbon source, ferrous sulfate heptahydrate (0.02g/L) is used as indicator, and agar concentration is 0.03g/L, prepare medium 100mL, Place in a Erlenmeyer flask with a cotton stopper, and sterilize under high temperature and high pressure (121° C., 15 minutes).
3.在培养基凝固以前,将三角烧瓶和富集液置于厌氧工作站的样品室中,抽氮气充氮气反复三次,抽走培养基内的空气。3. Before the culture medium is solidified, place the Erlenmeyer flask and the enrichment solution in the sample chamber of the anaerobic workstation, pump nitrogen and fill it with nitrogen repeatedly three times, and remove the air in the culture medium.
4.在厌氧工作站的操作箱中,在未凝固的培养基中接入3mL的富集上清液,摇匀后分装于厌氧管中。4. In the operation box of the anaerobic workstation, add 3mL of the enriched supernatant to the uncoagulated medium, shake well and distribute into anaerobic tubes.
5.将厌氧管取出,放入普通培养箱中,调节温度为15℃,24小时后,可观察到培养基内部有小黑点出现,继续培养2天,会有不同大小,出现先后时间不同的小黑点,用记号笔在管壁上标记。5. Take out the anaerobic tube, put it into an ordinary incubator, and adjust the temperature to 15°C. After 24 hours, small black spots can be observed inside the medium. Continue to cultivate for 2 days, there will be different sizes, and the time of appearance Different small black spots are marked on the tube wall with a marker pen.
6.将铜丝的一端砸平,将这段平的部分弯成钩状,用锡纸包好这样的一小捆铜丝后,灭菌。6. Flatten one end of the copper wire, bend the flat part into a hook shape, wrap such a small bundle of copper wire with tin foil, and then sterilize.
7.将灭菌的铜丝和厌氧管置于厌氧工作站中,用铜丝的弯的一端将小黑点挖出,接种于新的培养基即可。7. Place the sterilized copper wire and anaerobic tube in the anaerobic workstation, dig out the small black spots with the bent end of the copper wire, and inoculate them in new medium.
8.对分离得到的目的厌氧菌进行DNA的提取,在利用PCR做16s rDNA测序时不会出现双峰,测序结果准确,在NCBI数据库结果表明该菌与Thioclava pacifica最为相近,相似度100%。。8. Extract the DNA of the isolated target anaerobic bacteria. When PCR is used for 16s rDNA sequencing, no double peaks will appear, and the sequencing results are accurate. The results in the NCBI database show that the bacteria are most similar to Thioclava pacifica, with a similarity of 100%. . .
Claims (1)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2007100647153A CN101270334B (en) | 2007-03-23 | 2007-03-23 | Isolated culture method for anaerobic microorganism |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN2007100647153A CN101270334B (en) | 2007-03-23 | 2007-03-23 | Isolated culture method for anaerobic microorganism |
Publications (2)
Publication Number | Publication Date |
---|---|
CN101270334A CN101270334A (en) | 2008-09-24 |
CN101270334B true CN101270334B (en) | 2011-04-20 |
Family
ID=40004562
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN2007100647153A Expired - Fee Related CN101270334B (en) | 2007-03-23 | 2007-03-23 | Isolated culture method for anaerobic microorganism |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN101270334B (en) |
Families Citing this family (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101709267B (en) * | 2009-11-27 | 2011-08-31 | 中国科学院海洋研究所 | Method for quickly separating anaerobic micro-algae |
CN102424812B (en) * | 2011-12-30 | 2013-04-10 | 黑龙江八一农垦大学 | Method for separating cellulose-decomposing anaerobic bacteria from cellulose-decomposing composite bacterium strain |
CN104560771B (en) * | 2013-10-29 | 2017-08-22 | 中国石油化工股份有限公司 | A kind of isolated culture method of anaerobic bacteria |
CN106834102B (en) * | 2016-12-22 | 2019-08-02 | 中国科学院宁波城市环境观测研究站 | It cuts glue formula tubulose anaerobe and is separately cultured device and the anaerobe cultural method using the device |
CN113941305B (en) * | 2021-10-26 | 2022-11-22 | 南开大学 | Extraction method of extracellular polymer suitable for anaerobic bacteria |
CN114252322A (en) * | 2021-12-28 | 2022-03-29 | 何武顺 | Microorganism separation method for alkaline microorganism detection |
CN116064231B (en) * | 2023-03-06 | 2023-07-14 | 哈尔滨葵花药业有限公司 | Bifidobacterium culture equipment |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1415744A (en) * | 2001-10-29 | 2003-05-07 | 大庆油田有限责任公司 | Method for screening and separating microbial edge-water encroachment fungoid |
CN1827765A (en) * | 2006-01-23 | 2006-09-06 | 同济大学 | A screening method for anaerobic bacteria capable of degrading chlorophenols |
-
2007
- 2007-03-23 CN CN2007100647153A patent/CN101270334B/en not_active Expired - Fee Related
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1415744A (en) * | 2001-10-29 | 2003-05-07 | 大庆油田有限责任公司 | Method for screening and separating microbial edge-water encroachment fungoid |
CN1827765A (en) * | 2006-01-23 | 2006-09-06 | 同济大学 | A screening method for anaerobic bacteria capable of degrading chlorophenols |
Non-Patent Citations (5)
Title |
---|
JP特开2005-40029A 2005.02.17 |
李建秋 等.一次性厌氧菌培养平板的制备与实验使用.微生物学通报20 2.1993,20(2),121-122. |
李建秋等.一次性厌氧菌培养平板的制备与实验使用.微生物学通报20 2.1993,20(2),121-122. * |
李永峰 等.发酵产氢细菌分离培养的厌氧实验操作技术.哈尔滨工业大学学报36 12.2004,36(12),1589-1592. |
李永峰等.发酵产氢细菌分离培养的厌氧实验操作技术.哈尔滨工业大学学报36 12.2004,36(12),1589-1592. * |
Also Published As
Publication number | Publication date |
---|---|
CN101270334A (en) | 2008-09-24 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Ozuolmez et al. | Methanogenic archaea and sulfate reducing bacteria co-cultured on acetate: teamwork or coexistence? | |
CN101270334B (en) | Isolated culture method for anaerobic microorganism | |
Plugge | Anoxic media design, preparation, and considerations | |
Tanner | Cultivation of bacteria and fungi | |
Khelaifia et al. | A versatile medium for cultivating methanogenic archaea | |
Lackner et al. | Hydrogenotrophic methanogenesis and autotrophic growth of Methanosarcina thermophila | |
Sogodogo et al. | Methanogens as emerging pathogens in anaerobic abscesses | |
Pyzik et al. | Comparative analysis of deep sequenced methanogenic communities: identification of microorganisms responsible for methane production | |
Tian et al. | 16s rRNA gene sequencing and radioisotopic analysis reveal the composition of ammonia acclimatized methanogenic consortia | |
Hanišáková et al. | The historical development of cultivation techniques for methanogens and other strict anaerobes and their application in modern microbiology | |
CN104560777B (en) | High-tolerance aniline-degrading bacterium and application thereof | |
Siebert et al. | Estimation of methane-producing bacterial numbers by the most probable number (MPN) technique | |
El Houari et al. | Microbial communities and sulfate-reducing microorganisms abundance and diversity in municipal anaerobic sewage sludge digesters from a wastewater treatment plant (Marrakech, Morocco) | |
Kim et al. | Rapid isolation of fast-growing methanotrophs from environmental samples using continuous cultivation with gradually increased dilution rates | |
CN103881947A (en) | Brevendimonas diminuta strain for forming biofilm and application thereof in cyanide-containing wastewater treatment | |
Kim et al. | Structures of microbial communities found in anaerobic batch runs that produce methane from propionic acid—seeded from full-scale anaerobic digesters above a certain threshold | |
Haq et al. | Biogenic methane generation using solutions from column reactions of lignite with hydrogen peroxide | |
CN105647838A (en) | Acinetobacter pittii and application thereof | |
CN105670956A (en) | Medium thermophilic bacillus licheniformis strain and application thereof in treatment on high-temperature oil-bearing wastewater | |
Sekoai et al. | Elucidating the role of biofilm-forming microbial communities in fermentative biohydrogen process: an overview | |
CN204198730U (en) | Anerobe, microaerobe and need carbonic acid gas bacterium culture bag | |
Stams et al. | Citric acid wastewater as electron donor for biological sulfate reduction | |
CN106148218B (en) | Microecology of Photosynthetic Bacteria for Aquaculture and Its Application | |
Struk et al. | Modřice plant anaerobic digester: microbial distribution and biogas production | |
CN107760636B (en) | Denitrifying strain taking low-quality carbon source phenol as electron donor and application thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20110420 |
|
CF01 | Termination of patent right due to non-payment of annual fee |